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Uptake of Natural and Synthetic Estrogens by Maize Seedlings

机译:玉米幼苗对天然和合成雌激素的吸收

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Runoff from manure-fertilized crop fields constitutes a significant source of natural estrogens (e.g., estradiol [17β-E2] and estrone [El]) and synthetic estrogen mimics (e.g., zeranol [α-ZAL] and zearalanone [ZAN]) in the environment. However, processes such as sorption to and uptake by plants may inhibit the environmental mobility of hormonally active compounds. Sorption to dried root tissue was assessed in batch sorption tests, and resulting sorption isotherms were nonlinear at aqueous concentrations below 0.1 μM and linear above that limit. To evaluate the role of crop plants in the environmental fate of such compounds, we exposed hydroponic solutions containing 2 μM 17β-E2, El, α-ZAL, or ZAN to maize seedlings. After 22 days of exposure, α-ZAL and ZAN concentrations decreased by more than 96%, and 17β-E2 and El were undetectable. The decrease in α-ZAL and ZAN concentrations in maize-exposed solutions was initially slow, but the observed uptake exceeded that predicted by sorption alone within 3 d. All four estrogens were detected in root tissues at concentrations up to 0.19 μmol g~(-1), with concentrations peaking after 1—3 days of exposure. Only 17/7-E2 and a-ZAL were detected in shoots, and maximum concentrations were measured after 2 days for 17β-E2 (0.02 μmol g~(-1)) and 16 days for a-ZAL (0.8 nmol g~(-1)). Concentrations measured in root and shoot tissues were 82% or less than those predicted by a partition-limited uptake model, which is attributed to transformation and possibly irreversible binding processes.
机译:粪肥作物田地的径流是天然雌激素(例如,雌二醇[17β-E2]和雌酮[El])和合成雌激素模拟物(例如,山梨醇[α-ZAL]和泽拉拉酮[ZAN])的重要来源。环境。但是,诸如植物吸收和吸收等过程可能会抑制激素活性化合物的环境迁移。在分批的吸附测试中评估了对干燥的根组织的吸附,并且在水浓度低于0.1μM时,所产生的吸附等温线是非线性的,而在该极限值以上则呈线性。为了评估农作物在此类化合物的环境命运中的作用,我们将含有2μM17β-E2,E1,α-ZAL或ZAN的水培溶液暴露于玉米幼苗。暴露22天后,α-ZAL和ZAN浓度下降了96%以上,并且未检测到17β-E2和E1。玉米暴露溶液中α-ZAL和ZAN浓度的下降最初是缓慢的,但观察到的吸收超过了仅在3天内吸附所预测的吸收。在根组织中检出的所有四种雌激素浓度最高为0.19μmolg〜(-1),暴露后1-3天达到峰值。在芽中仅检测到17 / 7-E2和a-ZAL,在2天后测量17β-E2(0.02μmolg〜(-1))的最大浓度,在16天后测量a-ZAL(0.8 nmol g〜( -1))。在根和芽组织中测得的浓度比通过分区限制吸收模型预测的浓度低82%或更少,这归因于转化以及可能不可逆的结合过程。

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